BSEP116B Biodiversity in the Baltic Sea - Helcom
BSEP116B Biodiversity in the Baltic Sea - Helcom
BSEP116B Biodiversity in the Baltic Sea - Helcom
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Number of species<br />
16<br />
14<br />
12<br />
10<br />
8<br />
6<br />
4<br />
2<br />
0<br />
Tolypella<br />
Nitellopsis<br />
Nitella<br />
Lamprothamnium<br />
Chara<br />
of charophytes is found <strong>in</strong> <strong>the</strong> easternmost and<br />
nor<strong>the</strong>rnmost areas of <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> (Figure<br />
3.2.4.). The most common species <strong>in</strong> <strong>the</strong> <strong>Baltic</strong><br />
<strong>Sea</strong> is Chara aspera Willd. Chara baltica Bruzelius<br />
Kattegat W<br />
Danish Belts<br />
Kattegat E<br />
Øresund<br />
Zealand and Scania<br />
Gulf of Kiel<br />
Arkona <strong>Sea</strong> S<br />
Bornholm <strong>Sea</strong><br />
Hanö Bay<br />
Polish coast<br />
Gulf of Gdansk<br />
<strong>Baltic</strong> proper W<br />
Gotland <strong>Sea</strong><br />
<strong>Baltic</strong> proper E<br />
Gulf of Riga<br />
Estonian Arcipelago<br />
<strong>Baltic</strong> proper NW<br />
Gulf of F<strong>in</strong>land<br />
F<strong>in</strong>nish Archipelago <strong>Sea</strong><br />
Åland <strong>Sea</strong><br />
Bothnian <strong>Sea</strong><br />
Bothnian Bay<br />
Figure 3.2.4. Number of Charophyte species <strong>in</strong> different areas of <strong>the</strong><br />
<strong>Baltic</strong> <strong>Sea</strong>. Data from Schubert & Bl<strong>in</strong>dow 2003, Torn 2008. Division of<br />
<strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> after Nielsen et al. 1995.<br />
is also distributed all over <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> area and<br />
can be found on both sheltered and moderately<br />
exposed coastl<strong>in</strong>es. One of <strong>the</strong> rare species, Chara<br />
connivens Salzm. Ex A. Braun, is considered to<br />
have been brought to <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> by ballast sand<br />
and boulders <strong>in</strong> <strong>the</strong> sail<strong>in</strong>g ship era; it has a limited<br />
distribution <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>, but is abundant <strong>in</strong> <strong>the</strong><br />
areas <strong>in</strong> which it is found (Figure 3.2.5).<br />
In <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>, charophytes <strong>in</strong>habit mostly sheltered<br />
coastal areas, where <strong>the</strong>ir distribution pattern<br />
is primarily controlled by <strong>the</strong> sal<strong>in</strong>ity regime, settlement<br />
depth, sediment type and exposure (Schubert<br />
& Bl<strong>in</strong>dow 2003).<br />
In recent decades, <strong>the</strong> number of species, distribution<br />
area and biomass of charophytes have<br />
decl<strong>in</strong>ed significantly <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> (Schubert &<br />
Bl<strong>in</strong>dow 2003). Most of <strong>the</strong> records on <strong>the</strong> considerable<br />
decl<strong>in</strong>e of charophyte populations are from<br />
coastal waters of Schleswig-Holste<strong>in</strong>, <strong>the</strong> Swedish<br />
west coast and <strong>the</strong> coastal waters of Hanko pen<strong>in</strong>sula<br />
<strong>in</strong> southwestern F<strong>in</strong>land (Shubert & Bl<strong>in</strong>dow<br />
2003). The decl<strong>in</strong>e of charophytes is ma<strong>in</strong>ly caused<br />
by mechanical stress, comb<strong>in</strong>ed with <strong>the</strong> destruction<br />
of habitats and human-<strong>in</strong>duced pressures such<br />
as eutrophication.<br />
38<br />
Figure 3.2.5. Present distribution of <strong>in</strong>vasive Chara connivens <strong>in</strong> <strong>the</strong> <strong>Baltic</strong><br />
<strong>Sea</strong> (Torn 2008).<br />
Mytilus trossulus (Blue mussel)<br />
Two species of blue mussels can be found <strong>in</strong> <strong>the</strong><br />
<strong>Baltic</strong> <strong>Sea</strong> area. Mytilus edulis is distributed <strong>in</strong> <strong>the</strong><br />
North Atlantic and penetrates <strong>in</strong>to most of <strong>the</strong><br />
Kattegat. In <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>, Mytilus trossulus dom<strong>in</strong>ates<br />
<strong>the</strong> shallow, hard substrates <strong>in</strong> <strong>the</strong> deeper<br />
vegetation belt and below, with abundances up to<br />
36 000–156 000 <strong>in</strong>dividuals m −2 (Kautsky 1982). In<br />
<strong>the</strong> nor<strong>the</strong>rn <strong>Baltic</strong> Proper, blue mussels are most<br />
often found <strong>in</strong> <strong>the</strong> depth range 0–25 m (Westerbom<br />
2006); <strong>the</strong>y have <strong>the</strong>ir maximum between<br />
10–15 m depth (Littor<strong>in</strong> 1998) and usually start to<br />
decl<strong>in</strong>e after 30 m depth. Blue mussels dom<strong>in</strong>ate<br />
<strong>the</strong> animal biomass on hard substrates and, ow<strong>in</strong>g<br />
to <strong>the</strong>ir dom<strong>in</strong>ance, are considered to be one of<br />
key function<strong>in</strong>g species <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> Proper. Quantitatively,<br />
<strong>the</strong> blue mussel constitutes up to 80–90%<br />
of total animal biomass <strong>in</strong> <strong>the</strong> shallow areas of <strong>the</strong><br />
<strong>Baltic</strong> <strong>Sea</strong> (Kautsky et al. 1990). The blue mussel<br />
is considered to be an important l<strong>in</strong>k between<br />
<strong>the</strong> benthic and pelagic components of <strong>the</strong> <strong>Baltic</strong><br />
ecosystem, channell<strong>in</strong>g <strong>the</strong> flow of energy and<br />
matter, and be<strong>in</strong>g able to filter annually an amount